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Flora Biodiversity Assessment in Bonga, Boginda and Mankira Forest

Flora Biodiversity Assessment in Bonga, Boginda and Mankira Forest

Flora Biodiversity Assessment in Bonga, Boginda and Mankira Forest

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highly disturbed forest). In general about 92 tree/shrub/liana species above 10 cm<br />

diameter are recorded <strong>in</strong> the three study sites. On site specific basis 46, 70 <strong>and</strong> 54<br />

tree/shrub/liana species are recorded <strong>in</strong> <strong>Mankira</strong>, <strong>Bonga</strong> <strong>and</strong> Bog<strong>in</strong>da respectively.<br />

With respect to density of trees above 10 cm diameter <strong>Bonga</strong> forest has the highest<br />

(590), followed by Bog<strong>in</strong>da forest (575) <strong>and</strong> <strong>Mankira</strong> forest (454). A total of 57<br />

species <strong>in</strong> <strong>Bonga</strong>, 36 species <strong>in</strong> Bog<strong>in</strong>da <strong>and</strong> 30 species <strong>in</strong> <strong>Mankira</strong> are recorded as<br />

regeneration. In the current survey 61.4 percent of trees hav<strong>in</strong>g dbh greater or equal to<br />

10 cm are represented as regeneration <strong>in</strong> <strong>Bonga</strong>. In Bog<strong>in</strong>da 52.8 percent of<br />

trees/shrubs hav<strong>in</strong>g 10 cm <strong>and</strong> above are recorded as regeneration, whereas <strong>in</strong><br />

<strong>Mankira</strong>, 43.5 percent of trees greater than 10cm dbh are represented as regeneration.<br />

Species such as Cordia africana are not registered as regeneration <strong>in</strong> any of the three<br />

forest areas. This is probably because the species is an early colonizer (Friis1992).<br />

Croton macrostacheys too, as a pioneer species (light dem<strong>and</strong><strong>in</strong>g), does not get<br />

adequate conditions for regeneration <strong>in</strong> a natural forest (Denich, 2006). But on road<br />

sides <strong>and</strong> wherever there is an open<strong>in</strong>g, Croton macrostacheys is well grown <strong>and</strong><br />

observed. Ficus species are also not represented <strong>in</strong> regeneration except F. palmata <strong>in</strong><br />

<strong>Mankira</strong>. In total, <strong>in</strong>clud<strong>in</strong>g regeneration, sapl<strong>in</strong>gs, herbaceous plants <strong>and</strong> grasses<br />

<strong>Bonga</strong> forest has the largest plant cover per ha (estimated to be more than 1,309,956).<br />

<strong>Mankira</strong> <strong>and</strong> Bog<strong>in</strong>da have lower number of flora density, each compris<strong>in</strong>g 510,120<br />

<strong>and</strong> 386,600, respectively.<br />

d) Endemic plants recorded <strong>in</strong> the current study <strong>and</strong> Schmitt C. B. (2006) are listed as<br />

follows: Erythr<strong>in</strong>a brucei, Milletia ferrug<strong>in</strong>ea, Solanecio gigas, Tiliacora troup<strong>in</strong>ii,<br />

Vepris da<strong>in</strong>elli, Aframomum corrorima, Brillantaisia grotanellii, Satureja paradoxa,<br />

Vernonia tewoldei, Mikaniopsis clematoides, Lippia adoensis, Clematis longicauda,<br />

Clematis longicauda, Pilea bambuseti ssp aethiopica, Pentas tenuis, Dorstenia<br />

soerensenii, Phyllanthus limmuensis <strong>and</strong> Cyrtorchis ehrythraeae.<br />

e) The result of this survey <strong>in</strong>dicates absence of constantly present species with<strong>in</strong> the<br />

three forest sites which leads to the conclusion that each forest has a heterogeneous<br />

species composition. Croton macrostachyus <strong>in</strong> <strong>Mankira</strong>, Milletia ferrug<strong>in</strong>ea <strong>in</strong> <strong>Bonga</strong><br />

<strong>and</strong><br />

2

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